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' C,eolagical Tecknles frit. Page 4 <br /> Sinclair Trucking <br /> Feasibility Study Addendum <br /> Project No. 1030.3 <br /> April 26,2004 <br /> ' ORCs are magnesium peroxide compounds that slowly releases oxygen once it is hydrated. <br /> The byproducts of the reaction are oxygen and magnesium hydroxide. The material <br /> continues to release oxygen in the subsurface for approximately 6 months after application. <br /> ' The ORCs are installed using a GeoProbe direct push rig and a pressure pump. A series of <br /> borings are pushed to a detennined depth then a slurry of ORC is pumped through the drill <br /> rods under pressure as the rods are retrieved from the boring. The borings are drilled in a <br /> ' grid,pattern in the area of highest groundwater contamination. <br /> The application and cost of ORC and an AOP are very similar, however the AOP has the <br /> ' advantage because it is directly breaking down the contaminant where the ORC is only <br /> increasing oxygen to aid in bioremediation. Bioremediation is a relatively slow process that <br /> can be dependent on site conditions other then just oxygen levels. <br /> ' Site-specific Limitation <br /> It would seem that in situ remedial methods would be ideal, since the septic tank and leach <br /> line system would not have to be disturbed and the issue with fine grained soils and shallow <br /> groundwater could easily be dealt with. <br /> Site-specific Concern <br /> ' What is the potential effect of in situ ozone treatment for contaminated groundwater <br /> remediation on trees grown in close proximity to the treatment site? <br /> The potential effect of ozone gas in the vadose zone on trees, grasses, and other vegetative <br /> structures has not been well studied. However, certain assumptions can be made based on <br /> data produced from the field of phytoremediation and from agricultural studies, which have <br /> used ozone for plant treatment. The roots of trees are mostly concentrated in the upper 0.5- <br /> 1.5 ft of the surrounding soil, where the most oxygen and nutrients are found. The outer <br /> covering of the root contains mycorrhizae associated fungi, which are beneficial to the <br /> nutrition of the tree. Negative impacts of ozone gas in the vadose zone would most likely <br /> ' be due to the disinfecting properties of the ozone gas on root-associated fungi rather than on <br /> the tree root. Fairly high levels of ozone are required to disinfect fungi, and dosages of <br /> around 10-12 mgll are typical when using ozone to treat fungal contamination. <br /> ' Breakthrough levels of ozone at these levels have not been detected during in-situ <br /> remediation trials using high flows of pressurized ozone (personal communication, Chuck <br /> Whisman, Geological and Environmental Services, Exton, PA). In addition, a <br /> ' comprehensive study by the California Energy Commission (CEC) entitled "Integrated <br /> Agricultural Technology Demonstration", .Tune 1999, demonstrated the effect of using <br /> ozone gas in place of standard chemical treatments for bacterial and viral pathogens on <br /> ' agricultural crops. During these trials, the CEC showed that plants treated with 6% ozone <br /> gas, or with ozonated water, demonstrated increased plant yield and vigor. While this was <br /> partly due to the removal of the plant pathogens, the application of ozone as a treatment <br /> regime greatly enhanced the oxygen concentration in the irrigation water and soil. <br /> Treatment of contaminated groundwater with ozone would likely have the same positive <br /> effect on trees and other vegetation that are in proximity to the in-situ treatment site, due to <br /> the release of oxygen into the vadose zone during ozone treatment of the aquifer. <br />